CN104724678A - Method for fluidized catalytic decomposition of gypsum - Google Patents
Method for fluidized catalytic decomposition of gypsum Download PDFInfo
- Publication number
- CN104724678A CN104724678A CN201510089806.7A CN201510089806A CN104724678A CN 104724678 A CN104724678 A CN 104724678A CN 201510089806 A CN201510089806 A CN 201510089806A CN 104724678 A CN104724678 A CN 104724678A
- Authority
- CN
- China
- Prior art keywords
- gypsum
- sulfur
- gas phase
- calcium
- reducing agent
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 229910052602 gypsum Inorganic materials 0.000 title claims abstract description 75
- 239000010440 gypsum Substances 0.000 title claims abstract description 75
- 238000003421 catalytic decomposition reaction Methods 0.000 title claims abstract description 33
- 238000000034 method Methods 0.000 title claims abstract description 25
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims abstract description 95
- 239000011593 sulfur Substances 0.000 claims abstract description 92
- 229910052717 sulfur Inorganic materials 0.000 claims abstract description 92
- 239000012071 phase Substances 0.000 claims abstract description 52
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 38
- 239000003054 catalyst Substances 0.000 claims abstract description 32
- 239000007790 solid phase Substances 0.000 claims abstract description 28
- 239000002808 molecular sieve Substances 0.000 claims abstract description 22
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 claims abstract description 22
- 238000006243 chemical reaction Methods 0.000 claims abstract description 18
- 238000005406 washing Methods 0.000 claims abstract description 18
- 229910044991 metal oxide Inorganic materials 0.000 claims abstract description 17
- 150000004706 metal oxides Chemical class 0.000 claims abstract description 17
- 159000000007 calcium salts Chemical class 0.000 claims abstract description 12
- 239000000725 suspension Substances 0.000 claims abstract description 10
- 238000002360 preparation method Methods 0.000 claims abstract description 9
- 239000007789 gas Substances 0.000 claims description 66
- 239000000047 product Substances 0.000 claims description 23
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 claims description 20
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 claims description 20
- 239000000463 material Substances 0.000 claims description 18
- 239000002245 particle Substances 0.000 claims description 18
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 17
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 17
- 239000000843 powder Substances 0.000 claims description 17
- 239000002994 raw material Substances 0.000 claims description 15
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 12
- PASHVRUKOFIRIK-UHFFFAOYSA-L calcium sulfate dihydrate Chemical compound O.O.[Ca+2].[O-]S([O-])(=O)=O PASHVRUKOFIRIK-UHFFFAOYSA-L 0.000 claims description 12
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 10
- 229910000019 calcium carbonate Inorganic materials 0.000 claims description 10
- 239000001110 calcium chloride Substances 0.000 claims description 10
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 10
- FUFJGUQYACFECW-UHFFFAOYSA-L calcium hydrogenphosphate Chemical compound [Ca+2].OP([O-])([O-])=O FUFJGUQYACFECW-UHFFFAOYSA-L 0.000 claims description 10
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 9
- 239000000920 calcium hydroxide Substances 0.000 claims description 9
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 9
- 238000001035 drying Methods 0.000 claims description 9
- 239000007788 liquid Substances 0.000 claims description 9
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 8
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 6
- 238000004519 manufacturing process Methods 0.000 claims description 6
- 239000006227 byproduct Substances 0.000 claims description 5
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 claims description 5
- 230000003197 catalytic effect Effects 0.000 claims description 5
- 229910052759 nickel Inorganic materials 0.000 claims description 5
- 229910052742 iron Inorganic materials 0.000 claims description 4
- GYHNNYVSQQEPJS-UHFFFAOYSA-N Gallium Chemical compound [Ga] GYHNNYVSQQEPJS-UHFFFAOYSA-N 0.000 claims description 3
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 claims description 3
- 229910052925 anhydrite Inorganic materials 0.000 claims description 3
- 239000010941 cobalt Substances 0.000 claims description 3
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 3
- 239000010936 titanium Substances 0.000 claims description 3
- 239000004408 titanium dioxide Substances 0.000 claims description 3
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 claims description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 2
- 229910052804 chromium Inorganic materials 0.000 claims description 2
- 239000011651 chromium Substances 0.000 claims description 2
- 229910017052 cobalt Inorganic materials 0.000 claims description 2
- 239000004567 concrete Substances 0.000 claims description 2
- 229910052802 copper Inorganic materials 0.000 claims description 2
- 239000010949 copper Substances 0.000 claims description 2
- 229910052733 gallium Inorganic materials 0.000 claims description 2
- 229910052732 germanium Inorganic materials 0.000 claims description 2
- GNPVGFCGXDBREM-UHFFFAOYSA-N germanium atom Chemical compound [Ge] GNPVGFCGXDBREM-UHFFFAOYSA-N 0.000 claims description 2
- WPBNNNQJVZRUHP-UHFFFAOYSA-L manganese(2+);methyl n-[[2-(methoxycarbonylcarbamothioylamino)phenyl]carbamothioyl]carbamate;n-[2-(sulfidocarbothioylamino)ethyl]carbamodithioate Chemical compound [Mn+2].[S-]C(=S)NCCNC([S-])=S.COC(=O)NC(=S)NC1=CC=CC=C1NC(=S)NC(=O)OC WPBNNNQJVZRUHP-UHFFFAOYSA-L 0.000 claims description 2
- 229910052706 scandium Inorganic materials 0.000 claims description 2
- SIXSYDAISGFNSX-UHFFFAOYSA-N scandium atom Chemical compound [Sc] SIXSYDAISGFNSX-UHFFFAOYSA-N 0.000 claims description 2
- 239000012265 solid product Substances 0.000 claims description 2
- 229910052719 titanium Inorganic materials 0.000 claims description 2
- 229910052720 vanadium Inorganic materials 0.000 claims description 2
- 229910052725 zinc Inorganic materials 0.000 claims description 2
- 239000011701 zinc Substances 0.000 claims description 2
- 239000012530 fluid Substances 0.000 claims 6
- 239000003795 chemical substances by application Substances 0.000 claims 4
- 230000002829 reductive effect Effects 0.000 claims 4
- 239000005864 Sulphur Substances 0.000 claims 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims 3
- 206010013786 Dry skin Diseases 0.000 claims 1
- 239000004411 aluminium Substances 0.000 claims 1
- ZOMBKNNSYQHRCA-UHFFFAOYSA-J calcium sulfate hemihydrate Chemical compound O.[Ca+2].[Ca+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O ZOMBKNNSYQHRCA-UHFFFAOYSA-J 0.000 claims 1
- 150000001875 compounds Chemical class 0.000 claims 1
- 238000009833 condensation Methods 0.000 claims 1
- 230000005494 condensation Effects 0.000 claims 1
- -1 fluorgypsum Substances 0.000 claims 1
- 239000011507 gypsum plaster Substances 0.000 claims 1
- 239000011505 plaster Substances 0.000 claims 1
- 238000010025 steaming Methods 0.000 claims 1
- GPPXJZIENCGNKB-UHFFFAOYSA-N vanadium Chemical compound [V]#[V] GPPXJZIENCGNKB-UHFFFAOYSA-N 0.000 claims 1
- 239000003638 chemical reducing agent Substances 0.000 abstract description 36
- 238000000354 decomposition reaction Methods 0.000 abstract description 26
- 238000005265 energy consumption Methods 0.000 abstract description 5
- 230000007613 environmental effect Effects 0.000 abstract description 4
- 230000008569 process Effects 0.000 abstract description 4
- 230000008901 benefit Effects 0.000 abstract description 3
- 239000011575 calcium Substances 0.000 abstract description 2
- 239000011343 solid material Substances 0.000 abstract 1
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 50
- 238000004064 recycling Methods 0.000 description 32
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 22
- NBIIXXVUZAFLBC-UHFFFAOYSA-N phosphoric acid Substances OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 17
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 16
- 239000001569 carbon dioxide Substances 0.000 description 11
- 229910002092 carbon dioxide Inorganic materials 0.000 description 11
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 9
- JGIATAMCQXIDNZ-UHFFFAOYSA-N calcium sulfide Chemical compound [Ca]=S JGIATAMCQXIDNZ-UHFFFAOYSA-N 0.000 description 9
- 235000019700 dicalcium phosphate Nutrition 0.000 description 9
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 8
- 238000002309 gasification Methods 0.000 description 8
- 229910017604 nitric acid Inorganic materials 0.000 description 8
- 238000000926 separation method Methods 0.000 description 8
- 239000007792 gaseous phase Substances 0.000 description 6
- 238000005243 fluidization Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000000292 calcium oxide Substances 0.000 description 3
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 3
- 239000004568 cement Substances 0.000 description 3
- 238000010791 quenching Methods 0.000 description 3
- 238000006722 reduction reaction Methods 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-K Citrate Chemical compound [O-]C(=O)CC(O)(CC([O-])=O)C([O-])=O KRKNYBCHXYNGOX-UHFFFAOYSA-K 0.000 description 2
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 2
- 235000019738 Limestone Nutrition 0.000 description 2
- 235000011941 Tilia x europaea Nutrition 0.000 description 2
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 2
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 2
- 239000000378 calcium silicate Substances 0.000 description 2
- 229910052918 calcium silicate Inorganic materials 0.000 description 2
- OYACROKNLOSFPA-UHFFFAOYSA-N calcium;dioxido(oxo)silane Chemical compound [Ca+2].[O-][Si]([O-])=O OYACROKNLOSFPA-UHFFFAOYSA-N 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000003912 environmental pollution Methods 0.000 description 2
- 239000005431 greenhouse gas Substances 0.000 description 2
- AMWRITDGCCNYAT-UHFFFAOYSA-L hydroxy(oxo)manganese;manganese Chemical compound [Mn].O[Mn]=O.O[Mn]=O AMWRITDGCCNYAT-UHFFFAOYSA-L 0.000 description 2
- 239000004571 lime Substances 0.000 description 2
- 239000006028 limestone Substances 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- LEONUFNNVUYDNQ-UHFFFAOYSA-N vanadium atom Chemical compound [V] LEONUFNNVUYDNQ-UHFFFAOYSA-N 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 description 1
- 239000005751 Copper oxide Substances 0.000 description 1
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 description 1
- 240000007594 Oryza sativa Species 0.000 description 1
- 235000007164 Oryza sativa Nutrition 0.000 description 1
- WGLPBDUCMAPZCE-UHFFFAOYSA-N Trioxochromium Chemical compound O=[Cr](=O)=O WGLPBDUCMAPZCE-UHFFFAOYSA-N 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 229910000423 chromium oxide Inorganic materials 0.000 description 1
- 229910000428 cobalt oxide Inorganic materials 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 229910000431 copper oxide Inorganic materials 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 239000011737 fluorine Substances 0.000 description 1
- 229910052731 fluorine Inorganic materials 0.000 description 1
- 229910001195 gallium oxide Inorganic materials 0.000 description 1
- YBMRDBCBODYGJE-UHFFFAOYSA-N germanium oxide Inorganic materials O=[Ge]=O YBMRDBCBODYGJE-UHFFFAOYSA-N 0.000 description 1
- 239000010903 husk Substances 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 230000005012 migration Effects 0.000 description 1
- 238000013508 migration Methods 0.000 description 1
- 229910000480 nickel oxide Inorganic materials 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- PVADDRMAFCOOPC-UHFFFAOYSA-N oxogermanium Chemical compound [Ge]=O PVADDRMAFCOOPC-UHFFFAOYSA-N 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000004044 response Effects 0.000 description 1
- 235000009566 rice Nutrition 0.000 description 1
- HYXGAEYDKFCVMU-UHFFFAOYSA-N scandium oxide Chemical compound O=[Sc]O[Sc]=O HYXGAEYDKFCVMU-UHFFFAOYSA-N 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 1
- 229910001935 vanadium oxide Inorganic materials 0.000 description 1
- 239000011787 zinc oxide Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B17/00—Sulfur; Compounds thereof
- C01B17/02—Preparation of sulfur; Purification
- C01B17/12—Insoluble sulfur (mu-sulfur)
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B17/00—Sulfur; Compounds thereof
- C01B17/69—Sulfur trioxide; Sulfuric acid
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B25/00—Phosphorus; Compounds thereof
- C01B25/16—Oxyacids of phosphorus; Salts thereof
- C01B25/26—Phosphates
- C01B25/32—Phosphates of magnesium, calcium, strontium, or barium
- C01B25/322—Preparation by neutralisation of orthophosphoric acid
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/18—Carbonates
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/20—Halides
- C01F11/24—Chlorides
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/36—Nitrates
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
- C01P2006/00—Physical properties of inorganic compounds
- C01P2006/80—Compositional purity
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/584—Recycling of catalysts
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
本发明公开的一种流化催化分解石膏的方法,将石膏与金属氧化物分子筛催化剂混合均匀加入到流化反应器中,硫磺气从流化反应器底部进入与固体物料接触,反应分解石膏。反应得到的固相用蒸汽洗涤,洗涤后固相为金属氧化物分子筛催化剂,干燥后循环使用。洗涤后的气相冷凝得到Ca(OH)2悬浊液用于制备钙盐。未冷凝的气相可单独或与石膏分解反应后的气相产物中的SO2按克劳斯反应制备硫磺,作为还原剂循环使用。石膏分解反应得到的气相经过除尘,降温,经分离制备不溶性硫磺,可溶性硫磺作为还原剂循环使用。剩余的气相可与H2S制备硫磺再作为还原剂循环使用,或生产硫酸。本发明石膏分解能耗低,分解速率快,产品附加值高,工艺环保先进。
The invention discloses a method for fluidized catalytic decomposition of gypsum. The gypsum is uniformly mixed with a metal oxide molecular sieve catalyst and added to a fluidized reactor. Sulfur gas enters from the bottom of the fluidized reactor and contacts with solid materials to react and decompose the gypsum. The solid phase obtained by the reaction is washed with steam, and the solid phase after washing is a metal oxide molecular sieve catalyst, and is recycled after being dried. The washed gas phase was condensed to obtain a Ca(OH) suspension for the preparation of calcium salts. The uncondensed gas phase can be used alone or with SO2 in the gas phase product after the gypsum decomposition reaction to produce sulfur according to the Claus reaction, which can be recycled as a reducing agent. The gas phase obtained from the gypsum decomposition reaction is dedusted, cooled, separated to prepare insoluble sulfur, and the soluble sulfur is recycled as a reducing agent. The remaining gas phase can be combined with H 2 S to produce sulfur and then recycled as a reducing agent, or to produce sulfuric acid. The invention has the advantages of low energy consumption for decomposition of gypsum, fast decomposition rate, high added value of the product, and advanced environmental protection process.
Description
技术领域technical field
本发明涉及石膏资源利用技术领域,尤其涉及一种流化催化分解石膏的方法。The invention relates to the technical field of utilization of gypsum resources, in particular to a method for fluidized catalytic decomposition of gypsum.
背景技术Background technique
我国拥有丰富的天然石膏资源和巨量堆放的各类工业副产石膏资源,同时我国又面临硫资源匮乏和氧化钙资源主要以石灰石为原料的资源困境。我国硫资源产业尤其是硫酸的生产大量依赖于国外进口硫磺,使得整个产业的发展受制于人,充满风险。而以石灰石煅烧的方式获取氧化钙资源又大量排放温室气体二氧化碳,严重背离当前节能减排的环保趋势。分解石膏以分别获取硫、钙资源则能破解上述两个资源产业面临的难题。my country has abundant natural gypsum resources and various industrial by-product gypsum resources piled up in huge quantities. At the same time, my country is facing the resource dilemma of lack of sulfur resources and calcium oxide resources mainly using limestone as raw material. my country's sulfur resource industry, especially the production of sulfuric acid, relies heavily on imported sulfur from abroad, making the development of the entire industry subject to others and full of risks. However, obtaining calcium oxide resources by calcining limestone also emits a large amount of greenhouse gas carbon dioxide, which seriously deviates from the current environmental protection trend of energy conservation and emission reduction. Decomposing gypsum to obtain sulfur and calcium resources respectively can solve the problems faced by the above two resource industries.
在这样一类石膏分解的技术当中,最为典型的就是分解石膏制备硫酸联产水泥的工艺技术。特别是以磷石膏等工业副产石膏为原料时,还能使得硫元素以磷石膏—硫酸—磷酸的迁移方式获得循环利用。但是当前石膏分解技术还存在以下问题:石膏分解能耗高,分解速率慢,产品附加值低,污染环境,工艺落后。针对这一现状,近年来提出了一些新的技术方案。Among such gypsum decomposition technologies, the most typical one is the process technology of decomposing gypsum to prepare sulfuric acid co-production cement. Especially when the industrial by-product gypsum such as phosphogypsum is used as the raw material, the sulfur element can be recycled through the migration of phosphogypsum-sulfuric acid-phosphoric acid. However, the current gypsum decomposition technology still has the following problems: high energy consumption for gypsum decomposition, slow decomposition rate, low added value of products, environmental pollution, and backward technology. In response to this situation, some new technical solutions have been proposed in recent years.
中国发明专利ZL200910216325.2公布了一种硫磺还原分解磷石膏的方法,其特征在于先将磷石膏放入反应器中并在惰性氛围下,升温至500~900℃预热10~30分钟,然后通入摩尔分率为10~50%的气态硫磺与磷石膏进行还原反应1~2小时后,将所得硫化钙料块研磨后再与磷石膏按摩尔比1~1.5:3混合均匀,在非氧化性气氛中、1000~1400℃下焙烧0.5~3小时,所得固体渣料中CaO作为水泥熟料用于水泥生产,所产生的尾气SO2作为生产硫酸的原料气。Chinese invention patent ZL200910216325.2 discloses a method for reducing and decomposing phosphogypsum by sulfur, which is characterized in that the phosphogypsum is first put into a reactor and heated to 500-900°C for 10-30 minutes under an inert atmosphere, and then Feed in gaseous sulfur with a molar fraction of 10-50% and phosphogypsum for reduction reaction for 1-2 hours, grind the obtained calcium sulfide block and then mix it with phosphogypsum at a molar ratio of 1-1.5:3. Roasting at 1000-1400°C for 0.5-3 hours in an oxidizing atmosphere, the CaO in the obtained solid slag is used as cement clinker for cement production, and the generated tail gas SO 2 is used as raw material gas for sulfuric acid production.
中国发明专利ZL201010223874.5公布了一种磷石膏振动流态化分解的方法。其特征在于将复合外加剂与预处理后的磷石膏按照质量比1:7混合均匀,送入窑外均匀流态化分解炉,在Ar气氛保护下升温至850~1100℃,然后以5~50ml/min的流量通入CO,并使CO与Ar的体积流量比为1:(2~19),控制温度为850~1100℃,启动振动能量载入装置,进行还原分解。Chinese invention patent ZL201010223874.5 discloses a method for vibrating fluidized decomposition of phosphogypsum. It is characterized in that the composite admixture and the pretreated phosphogypsum are mixed evenly according to the mass ratio of 1:7, and sent to the uniform fluidized decomposition furnace outside the kiln, and the temperature is raised to 850-1100 °C under the protection of Ar atmosphere, and then the temperature is 5-100 °C. The flow rate of 50ml/min is passed into CO, and the volume flow ratio of CO and Ar is 1:(2~19), the temperature is controlled at 850~1100°C, and the vibration energy loading device is started for reduction and decomposition.
中国发明专利申请CN103864024A公布了一种催化分解磷石膏的方法,其技术方案为:将磷石膏和炭化稻壳按质量比(20~1):1混合均匀,制得混合料。再将所述的混合料放入管式炉中,在600~900℃条件下进行催化分解反应,反应时间为60~180min,反应得到的二氧化硫气体直接制硫酸,反应得到的固体产物为活性石灰、或为硅酸钙、或为活性石灰和硅酸钙。Chinese invention patent application CN103864024A discloses a method for catalytically decomposing phosphogypsum. The technical solution is: mix phosphogypsum and carbonized rice husk uniformly in a mass ratio (20-1):1 to prepare a mixture. Then put the mixture into a tube furnace, and carry out a catalytic decomposition reaction at 600-900°C. The reaction time is 60-180min. The sulfur dioxide gas obtained by the reaction is directly produced into sulfuric acid, and the solid product obtained by the reaction is active lime. , or calcium silicate, or active lime and calcium silicate.
上述技术方案在解决石膏分解技术存在的分解能耗高,分解速率慢,污染环境,工艺落后等方面有一定贡献,但都不全面,并且都存在产品附加值低,不能使技术方案获得良好经济效益的缺点。The above-mentioned technical solutions have made certain contributions in solving the problems of high decomposition energy consumption, slow decomposition rate, environmental pollution, and backward technology of gypsum decomposition technology, but they are not comprehensive, and all of them have low added value of products, which cannot make the technical solutions obtain good economic benefits. Shortcomings.
发明内容Contents of the invention
本发明目的在于提出一种能够全面解决上述石膏分解技术存在的各种缺点的石膏分解新方法。The purpose of the present invention is to propose a new method for gypsum decomposition that can comprehensively solve the various shortcomings of the above-mentioned gypsum decomposition technology.
本发明采用如下技术方案:The present invention adopts following technical scheme:
本发明的流化催化分解石膏的方法的具体步骤如下:The concrete steps of the method for fluidized catalytic decomposition of gypsum of the present invention are as follows:
(1)、粉状的石膏原料与金属氧化物分子筛催化剂颗粒按照质量比(1~30):1混合均匀,加入到流化反应器中;(1), the powdery gypsum raw material and the metal oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio (1-30): 1, and then added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比(2~10):1,气相摩尔分率10%~100%,从流化反应器底部进入,与(1)中物料接触,在480℃~700℃分解石膏,物料停留时间在1~60min,石膏分解率为60%~100%。(2), the sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor according to the mass ratio (2 to 10): 1 with the gypsum powder, and the gas phase molar fraction is 10% to 100%. During material contact, the gypsum is decomposed at 480°C-700°C, the residence time of the material is 1-60min, and the decomposition rate of gypsum is 60%-100%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为40%~100%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在120℃~200℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为20%~60%的悬浊液,再与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为80%~100%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase (calcium sulfide mass fraction is 40%~100% powder and catalyst particle) that fluidized catalytic decomposition reaction obtains carries out steam washing, and the solid phase after washing is metal oxide molecular sieve catalyst, at 120 ℃~200℃ and return to step (1) for recycling after drying. The gas phase is condensed first to obtain a suspension with a mass fraction of calcium hydroxide of 20% to 60%, and then reacts with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium carbonate, calcium nitrate, calcium hydrogen phosphate, calcium chloride, etc. Salt. The uncondensed gas phase (with a hydrogen sulfide mole fraction of 80% to 100%) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent .
(4)、流化催化分解反应得到的480℃~700℃的气相(二氧化硫摩尔分率为6%~20%,硫磺气摩尔分率为5%~80%)经过除尘,降温至120℃~150℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥98%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为5%~30%)再与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺并返回系统作为还原剂循环使用,或生产硫酸。(4) The gas phase at 480°C to 700°C (the molar fraction of sulfur dioxide is 6% to 20%, and the molar fraction of sulfur gas is 5% to 80%) obtained from the fluidized catalytic decomposition reaction is dedusted and cooled to 120°C to At 150°C, the gaseous sulfur is quenched into liquid sulfur, and insoluble sulfur with a purity ≥ 98% is prepared by separation, while the soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (mole fraction of sulfur dioxide is 5% to 30%) is then washed with the solid phase product to obtain hydrogen sulfide through Claus reaction to produce sulfur and return to the system as a reducing agent for recycling, or to produce sulfuric acid.
步骤(1)中,所述的石膏原料为为天然石膏、硬石膏、磷石膏、脱硫石膏、氟石膏、柠檬酸石膏、镍石膏、盐石膏或钛白粉副产石膏中的一种或几种。In step (1), the gypsum raw material is one or more of natural gypsum, anhydrite, phosphogypsum, desulfurized gypsum, fluorine gypsum, citrate gypsum, nickel gypsum, salt gypsum or titanium dioxide by-product gypsum .
步骤(1)中,所述的金属氧化物分子筛催化剂所含金属氧化物成分为钪、钛、钒、铬、锰、铁、钴、镍、铜、锌、铝、镓或锗的氧化物中的一种或几种。In step (1), the metal oxide component contained in the metal oxide molecular sieve catalyst is the oxide of scandium, titanium, vanadium, chromium, manganese, iron, cobalt, nickel, copper, zinc, aluminum, gallium or germanium one or more of.
最终产品为不溶性硫磺,硫酸和碳酸钙、硝酸钙、磷酸氢钙、氯化钙这几种钙盐中的至少一种。The final product is insoluble sulfur, sulfuric acid and at least one of these calcium salts of calcium carbonate, calcium nitrate, calcium hydrogen phosphate and calcium chloride.
本发明的流化催化分解石膏的方法具有分解能耗低,分解速率快,产品附加值高,工艺环保先进的优点。The method for decomposing gypsum by fluidization catalysis of the present invention has the advantages of low decomposition energy consumption, fast decomposition rate, high added value of products, and advanced environmental protection technology.
本发明与现有技术相比,具有以下显著特征和有益效果:Compared with the prior art, the present invention has the following remarkable features and beneficial effects:
1.采用流化催化的分解方法,通过强化反应传质和降低反应能垒,达到明显降低反应能耗,加快反应速率的效果。1. Using the fluidized catalytic decomposition method, by strengthening the mass transfer of the reaction and reducing the energy barrier of the reaction, the effect of significantly reducing the energy consumption of the reaction and accelerating the reaction rate is achieved.
2.本方法中流化与催化相互耦合,硫磺既是还原剂又是流化介质,催化剂既起到催化作用又能有效改善石膏颗粒的流化性能,这是现有技术无法实现的。2. Fluidization and catalysis are coupled with each other in this method. Sulfur is both a reducing agent and a fluidization medium. The catalyst can not only play a catalytic role but also effectively improve the fluidization performance of gypsum particles, which cannot be realized by the prior art.
3.通过制备高附加值的不溶性硫磺及精细钙盐等产品,提升产品价值,使本方法具备很强的技术经济竞争力。3. By preparing products such as high value-added insoluble sulfur and fine calcium salt, the value of the product is improved, so that the method has strong technical and economic competitiveness.
4.相比已有技术方案,本方法在分解石膏过程中不但不排放二氧化碳等温室气体,而且还能吸收利用二氧化碳,具备零碳排放的优异环保特性。4. Compared with the existing technical solutions, this method not only does not emit greenhouse gases such as carbon dioxide in the process of decomposing gypsum, but also absorbs and utilizes carbon dioxide, and has excellent environmental protection characteristics of zero carbon emissions.
5.本方法中催化剂可重复利用,中间产物可制备及回收原料硫磺,产品硫酸可实现硫酸→石膏→硫酸的产业链循环,因此相比现有方案,具备突出的循环经济特效。5. In this method, the catalyst can be reused, the intermediate product can be used to prepare and recover the raw material sulfur, and the product sulfuric acid can realize the industrial chain cycle of sulfuric acid → gypsum → sulfuric acid. Therefore, compared with the existing scheme, it has outstanding circular economy effects.
附图说明Description of drawings
图1是本发明的流化催化分解石膏的方法的工艺流程图。Fig. 1 is a process flow chart of the method for fluidized catalytic decomposition of gypsum of the present invention.
具体实施方式Detailed ways
下面通过实施例对本发明进行具体的描述,有必要在此指出的是本实施例只用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,该领域的技术熟练人员根据上述本发明内容对本发明所作的一些非本质的改进和调整仍应属于本发明的保护范围。The present invention is specifically described below through the examples, it is necessary to point out that the present examples are only used to further illustrate the present invention, and can not be interpreted as limiting the protection scope of the present invention, those skilled in the art according to the above-mentioned present invention Contents Some non-essential improvements and adjustments made to the present invention should still belong to the protection scope of the present invention.
实施例1Example 1
(1)、粉状的天然石膏或硬石膏原料与铁或钪氧化物分子筛催化剂颗粒按照质量比1:1混合均匀,加入到流化反应器中;(1), powdered natural gypsum or anhydrite raw material and iron or scandium oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 1:1, and then added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比2:1,气相摩尔分率10%,从流化反应器底部进入,与(1)中物料接触,在550℃分解石膏,物料停留时间在1min,石膏分解率为60%。(2) Sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 2:1 to gypsum powder and a mole fraction of the gas phase of 10%, and contacts with the material in (1), at 550°C To decompose gypsum, the residence time of the material is 1min, and the decomposition rate of gypsum is 60%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为40%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在120℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为20%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为80%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 40% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 120 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 20%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (containing hydrogen sulfide with a mole fraction of 80%) can be used alone or with sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的550℃的气相(二氧化硫摩尔分率为6%,硫磺气摩尔分率为80%)经过除尘,降温至150℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥98%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为30%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 550 ℃ gaseous phase (sulfur dioxide molar fraction is 6%, sulfur gas molar fraction is 80%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 150 ℃, makes gaseous sulfur quench to be liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 98%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 30%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例2Example 2
(1)、粉状的脱硫石膏或盐石膏原料与钛或锰氧化物分子筛催化剂颗粒按照质量比10:1混合均匀,加入到流化反应器中;(1), powdery desulfurization gypsum or salt gypsum raw material and titanium or manganese oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 10:1, and then added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比3:1,气相摩尔分率40%,从流化反应器底部进入,与(1)中物料接触,在600℃分解石膏,物料停留时间在10min,石膏分解率为80%。(2) Sulfur gas after gasification of sulfur as a reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 3:1 to gypsum powder and a mole fraction of the gas phase of 40%, and contacts with the material in (1), at 600°C Decompose gypsum, the material residence time is 10min, and the gypsum decomposition rate is 80%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为70%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在150℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为30%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为85%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 70% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 150 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 30%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium carbonate, calcium nitrate, calcium hydrogen phosphate, calcium chloride and other calcium salts. The uncondensed gas phase (containing hydrogen sulfide with a mole fraction of 85%) can be used alone or with sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的600℃的气相(二氧化硫摩尔分率为8%,硫磺气摩尔分率为60%)经过除尘,降温至130℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥99%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为15%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 600 DEG C gaseous phase (sulfur dioxide molar fraction is 8%, sulfur gas molar fraction is 60%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 130 DEG C, makes gaseous state sulfur be quenched into liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 99%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 15%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例3Example 3
(1)、粉状的钛白粉副产石膏原料与钒或铬氧化物分子筛催化剂颗粒按照质量比5:1混合均匀,加入到流化反应器中;(1), powdery titanium dioxide by-product gypsum raw material and vanadium or chromium oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 5:1, and added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比6:1,气相摩尔分率50%,从流化反应器底部进入,与(1)中物料接触,在620℃分解石膏,物料停留时间在20min,石膏分解率为90%。(2) Sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 6:1 to gypsum powder and a mole fraction of the gas phase of 50%, and contacts with the material in (1), at 620°C Decompose gypsum, the material residence time is 20min, and the gypsum decomposition rate is 90%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为95%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在180℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为45%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为95%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 95% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 180 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 45%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (with a hydrogen sulfide molar fraction of 95%) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的620℃的气相(二氧化硫摩尔分率为12%,硫磺气摩尔分率为55%)经过除尘,降温至145℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥98.5%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为10%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the gas phase of 620 DEG C obtained by fluidized catalytic decomposition reaction (the molar fraction of sulfur dioxide is 12%, the molar fraction of sulfur gas is 55%) is dedusted, cooled to 145 DEG C, the gaseous sulfur is quenched into liquid sulfur, and the Separation and preparation of insoluble sulfur with a purity ≥ 98.5%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 10%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例4Example 4
(1)、粉状的磷石膏原料与铁或铝氧化物分子筛催化剂颗粒按照质量比20:1混合均匀,加入到流化反应器中;(1), powdery phosphogypsum raw material and iron or aluminum oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 20:1, and then added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比7:1,气相摩尔分率30%,从流化反应器底部进入,与(1)中物料接触,在650℃分解石膏,物料停留时间在5min,石膏分解率为100%。(2) Sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 7:1 to gypsum powder and a gas phase molar fraction of 30%, and contacts with the material in (1), at 650°C To decompose gypsum, the material residence time is 5 minutes, and the gypsum decomposition rate is 100%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为100%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在200℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为60%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为100%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase (calcium sulfide mass fraction is 100% powder and catalyst particles) obtained by fluidized catalytic decomposition reaction is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 200 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 60%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (100% mole fraction of hydrogen sulfide) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的650℃的气相(二氧化硫摩尔分率为20%,硫磺气摩尔分率为50%)经过除尘,降温至120℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥99.5%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为5%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 650 DEG C gaseous phase (sulfur dioxide molar fraction is 20%, sulfur gas molar fraction is 50%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 120 DEG C, makes gaseous sulfur quick-cooling is liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 99.5%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 5%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例5Example 5
(1)、粉状的柠檬酸石膏原料与钴或铜氧化物分子筛催化剂颗粒按照质量比15:1混合均匀,加入到流化反应器中;(1), powdery citrate gypsum raw material and cobalt or copper oxide molecular sieve catalyst particles are mixed evenly according to mass ratio 15:1, join in the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比10:1,气相摩尔分率70%,从流化反应器底部进入,与(1)中物料接触,在700℃分解石膏,物料停留时间在15min,石膏分解率为95%。(2) The sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 10:1 to gypsum powder and a gas phase molar fraction of 70%, and contacts with the material in (1), at 700°C To decompose gypsum, the material residence time is 15 minutes, and the gypsum decomposition rate is 95%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为98%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在150℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为50%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为90%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 98% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 150 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 50%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (with a hydrogen sulfide molar fraction of 90%) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的700℃的气相(二氧化硫摩尔分率为16%,硫磺气摩尔分率为58%)经过除尘,降温至125℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥99%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为12%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 700 DEG C gaseous phase (sulfur dioxide molar fraction is 16%, sulfur gas molar fraction is 58%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 125 DEG C, makes gaseous sulfur quench to be liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 99%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 12%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例6Example 6
(1)、粉状的镍石膏原料与镍或锌氧化物分子筛催化剂颗粒按照质量比30:1混合均匀,加入到流化反应器中;(1), powdery nickel gypsum raw material and nickel or zinc oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 30:1, and then added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比4:1,气相摩尔分率100%,从流化反应器底部进入,与(1)中物料接触,在480℃分解石膏,物料停留时间在60min,石膏分解率为90%。(2) The sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor according to the mass ratio of 4:1 to gypsum powder, and the molar fraction of the gas phase is 100%, and contacts with the material in (1), at 480°C Decompose gypsum, the material residence time is 60min, and the gypsum decomposition rate is 90%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为95%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在120℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为45%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为98%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 95% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 120 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 45%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (with a hydrogen sulfide molar fraction of 98%) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的480℃的气相(二氧化硫摩尔分率为12%,硫磺气摩尔分率为55%)经过除尘,降温至140℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥98%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为10%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 480 DEG C gaseous phase (sulfur dioxide molar fraction is 12%, sulfur gas molar fraction is 55%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 140 DEG C, makes gaseous sulfur quick-cooling is liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 98%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 10%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
实施例7Example 7
(1)、粉状的氟石膏原料与镓或锗氧化物分子筛催化剂颗粒按照质量比15:1混合均匀,加入到流化反应器中;(1), powdery fluorogypsum raw material and gallium or germanium oxide molecular sieve catalyst particles are mixed evenly according to the mass ratio of 15:1, and added to the fluidized reactor;
(2)、还原剂硫磺气化后的硫磺气按照与石膏粉的质量比8:1,气相摩尔分率60%,从流化反应器底部进入,与(1)中物料接触,在680℃分解石膏,物料停留时间在30min,石膏分解率为95%。(2) The sulfur gas after sulfur gasification of the reducing agent enters from the bottom of the fluidized reactor at a mass ratio of 8:1 to gypsum powder and a gas phase molar fraction of 60%, and contacts with the material in (1), at 680°C Decompose gypsum, the material residence time is 30min, and the gypsum decomposition rate is 95%.
(3)、流化催化分解反应得到的固相(硫化钙质量分率为98%的粉料和催化剂颗粒)进行蒸汽洗涤,洗涤后的固相为金属氧化物分子筛催化剂,在180℃干燥后返回第(1)步循环使用。而气相先冷凝,得到氢氧化钙质量分率为50%的悬浊液,可与二氧化碳、硝酸、磷酸、盐酸等反应生产碳酸钙、硝酸钙、磷酸氢钙、氯化钙等钙盐。未冷凝的气相(含硫化氢摩尔分率为96%)可单独或者与流化催化分解反应后的气相产物中的二氧化硫按克劳斯反应制备硫磺,再返回系统作为还原剂循环使用。(3), the solid phase obtained by the fluidized catalytic decomposition reaction (calcium sulfide mass fraction is 98% powder and catalyst particles) is steam washed, and the solid phase after washing is a metal oxide molecular sieve catalyst, after drying at 180 ° C Return to step (1) for recycling. The gas phase is first condensed to obtain a suspension with a mass fraction of calcium hydroxide of 50%, which can be reacted with carbon dioxide, nitric acid, phosphoric acid, hydrochloric acid, etc. to produce calcium salts such as calcium carbonate, calcium nitrate, calcium hydrogen phosphate, and calcium chloride. The uncondensed gas phase (with a hydrogen sulfide molar fraction of 96%) can be used alone or with the sulfur dioxide in the gas phase product after the fluidized catalytic decomposition reaction to produce sulfur by Claus reaction, and then returned to the system for recycling as a reducing agent.
(4)、流化催化分解反应得到的680℃的气相(二氧化硫摩尔分率为16%,硫磺气摩尔分率为58%)经过除尘,降温至135℃,使气态硫磺急冷为液态硫磺,经分离制备纯度≥98.5%的不溶性硫磺,而可溶性硫磺则返回系统作为还原剂循环使用。剩余的气相(二氧化硫摩尔分率为12%)可部分与固相产物洗涤后得到的硫化氢经克劳斯反应制备硫磺再返回系统作为还原剂循环使用,另一部分则可生产硫酸。(4), the 680 ℃ gaseous phase (the molar fraction of sulfur dioxide is 16%, the molar fraction of sulfur gas is 58%) that the fluidized catalytic decomposition reaction obtains is through dedusting, is cooled to 135 ℃, makes gaseous sulfur quench to be liquid sulfur, through Separation and preparation of insoluble sulfur with a purity ≥ 98.5%, while soluble sulfur is returned to the system as a reducing agent for recycling. The remaining gas phase (the molar fraction of sulfur dioxide is 12%) can be partially reacted with the hydrogen sulfide obtained after washing the solid phase product to produce sulfur and then returned to the system for recycling as a reducing agent, and the other part can be used to produce sulfuric acid.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510089806.7A CN104724678B (en) | 2015-02-27 | 2015-02-27 | A method for fluidized catalytic decomposition of gypsum |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510089806.7A CN104724678B (en) | 2015-02-27 | 2015-02-27 | A method for fluidized catalytic decomposition of gypsum |
Publications (2)
Publication Number | Publication Date |
---|---|
CN104724678A true CN104724678A (en) | 2015-06-24 |
CN104724678B CN104724678B (en) | 2018-07-06 |
Family
ID=53449183
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510089806.7A Expired - Fee Related CN104724678B (en) | 2015-02-27 | 2015-02-27 | A method for fluidized catalytic decomposition of gypsum |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN104724678B (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105858620A (en) * | 2016-05-20 | 2016-08-17 | 四川大学 | Method for decomposing gypsum through synergistic fluidization |
CN106829876A (en) * | 2017-03-02 | 2017-06-13 | 洛阳九成新材料技术有限公司 | The recoverying and utilizing method of oil plant sulfur removal plant sulphur steam |
CN112191240A (en) * | 2020-09-16 | 2021-01-08 | 福泉环保城发展有限公司 | Industrial phosphogypsum waste treatment method |
CN113200559A (en) * | 2021-04-28 | 2021-08-03 | 襄阳泽东化工集团有限公司 | Method for preparing superfine calcium carbonate by using phosphogypsum and decarbonization analysis gas |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101708826A (en) * | 2009-11-25 | 2010-05-19 | 四川大学 | Method for reducing and decomposing phosphogypsum by sulfur |
CN101708825A (en) * | 2009-11-25 | 2010-05-19 | 四川大学 | Method for preparing calcium sulfide by reducing and decomposting gypsum through sulfur |
CN103408052A (en) * | 2013-07-25 | 2013-11-27 | 昆明理工大学 | Decomposition method of ardealite |
CN103466675A (en) * | 2013-09-03 | 2013-12-25 | 昆明理工大学 | Decomposition method of ardealite |
-
2015
- 2015-02-27 CN CN201510089806.7A patent/CN104724678B/en not_active Expired - Fee Related
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101708826A (en) * | 2009-11-25 | 2010-05-19 | 四川大学 | Method for reducing and decomposing phosphogypsum by sulfur |
CN101708825A (en) * | 2009-11-25 | 2010-05-19 | 四川大学 | Method for preparing calcium sulfide by reducing and decomposting gypsum through sulfur |
CN103408052A (en) * | 2013-07-25 | 2013-11-27 | 昆明理工大学 | Decomposition method of ardealite |
CN103466675A (en) * | 2013-09-03 | 2013-12-25 | 昆明理工大学 | Decomposition method of ardealite |
Non-Patent Citations (2)
Title |
---|
钟本和 等: ""我国磷石膏利用途径的探讨"", 《磷肥与复肥》 * |
钟本和: ""硫磺还原分解磷石膏制硫酸节能减排新工艺"", 《化肥工业》 * |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105858620A (en) * | 2016-05-20 | 2016-08-17 | 四川大学 | Method for decomposing gypsum through synergistic fluidization |
CN106829876A (en) * | 2017-03-02 | 2017-06-13 | 洛阳九成新材料技术有限公司 | The recoverying and utilizing method of oil plant sulfur removal plant sulphur steam |
CN106829876B (en) * | 2017-03-02 | 2018-09-04 | 洛阳九成新材料技术有限公司 | The recoverying and utilizing method of oil plant sulfur removal plant sulphur steam |
CN112191240A (en) * | 2020-09-16 | 2021-01-08 | 福泉环保城发展有限公司 | Industrial phosphogypsum waste treatment method |
CN112191240B (en) * | 2020-09-16 | 2023-02-10 | 福泉环保城发展有限公司 | Industrial phosphogypsum waste treatment method |
CN113200559A (en) * | 2021-04-28 | 2021-08-03 | 襄阳泽东化工集团有限公司 | Method for preparing superfine calcium carbonate by using phosphogypsum and decarbonization analysis gas |
Also Published As
Publication number | Publication date |
---|---|
CN104724678B (en) | 2018-07-06 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102502524B (en) | Method for producing sulfur dioxide from calcium sulfate and sulfur | |
CN104724678B (en) | A method for fluidized catalytic decomposition of gypsum | |
CN103408052B (en) | A kind of decomposition method of phosphogypsum | |
CN103864150A (en) | The preparation method of calcium ferrite | |
CN101955166B (en) | Method for decomposing semi-hydrated phosphogypsum | |
CN102530889A (en) | Method for preparing sulfuric acid by reducing and decomposing gypsum with pyrite | |
CN101244811B (en) | Method for improving SO2 concentration in acid making technique with decomposition of calcium sulphate | |
CN101708825B (en) | Method for preparing calcium sulfide by reducing and decomposting gypsum through sulfur | |
CN105272340B (en) | A kind of method that decomposing phosphogypsum prepares silico-calcium matter porous ceramic grain and sulfuric acid | |
CN101434390B (en) | Method for producing calcium carbide and sulphuric acid using industry by-product gypsum | |
CN113120933B (en) | A process and system for preparing quicklime based on carbon emission reduction | |
CN103864024A (en) | Method for catalytic decomposition of phosphogypsum | |
CN103818884B (en) | The spouted fluidized decomposition technique of a kind of gypsum | |
CN101462698B (en) | Industrial method for cyclic utilization of ironmaking production desulfurized gypsum and blast furnace gas | |
CN103466675B (en) | Decomposition method of ardealite | |
CN113603126A (en) | Method for preparing calcium oxide by using industrial byproduct gypsum | |
CN103193206A (en) | A kind of method that sulfur reduction decomposes sulfate to produce SO2 | |
CN102020250A (en) | New method for producing sulphuric acid and generation joint product cement by decomposing phosphogypsum through microwave reduction | |
CN103303875A (en) | Method for recovering pyrite resources | |
CN102320640A (en) | Method for decomposing phosphogypsum through coupling reaction heat and vibration fluidizing | |
CN103864023B (en) | A kind of method of ardealite carbonating tail gas reducing and decomposing phosphogypsum | |
CN106755958A (en) | A kind of method that Rock coal containing alum is calcined vanadium extraction | |
CN103539091A (en) | Method for preparing phosphoric acid by catalytic reduction of low-medium-grade phosphorite | |
CN101941806A (en) | Method for utilizing composite reducing agent to decompose phosphogypsum | |
CN107935006A (en) | Method for extracting aluminum oxide by mixing and roasting ammonium sulfate and fly ash in reducing atmosphere |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20180706 Termination date: 20210227 |